Saturday, 26 August 2017

The Danger of using Picloram in Environmentally Sensitive Areas

In 2013 I first began noticing what was
very clearly herbicide damage and death being caused in particular to two
species of tree being Grewia occidentalis and Trema orientalis. I took photos of
the affected trees but could not establish the source of or the herbicide that
had caused the damage.

Trema orientalis that has been damaged by a very small dose of the herbicide picloram

More and more I began noticing trees that
had been affected or had been killed by what was very clearly as the result of
herbicide poisoning but again I could not establish what herbicide had caused
the death of the trees and when the spraying had occurred, in some areas the
last spraying had occurred a few years previously.

About a year after first observing the
herbicide damage to trees and other plants I accidentally discovered the
culprit herbicide.

I had removed a narrow band of bark down to
the cambium on three trees on my property and carefully applied a very narrow
band of Kaput Gel containing Triclopyr and Picloram in a band of about 50 mm on
the bottom half of the area where the bark had been removed. Within a few days
I noticed that two trees growing within a few meters of one of the trees
started to show signs of herbicide poisoning and within two weeks one of the
small trees Hippobromus pauciflorus was completely dead, the second small tree
affected was Obetia tenax which very nearly died but eventually after more than
three years recovered. For up to three meters along the line of the main roots
all dicotyledonous ground cover plants were affected. A wild grape Rhoicissus
tomentosa growing about six meters from one of the other trees was also very
badly affected clearly from herbicide leached from the tree that had been
treated with Kaput gel, eventually over ninety percent of the very large vine
died what is left at the time of writing being August 2017 has not completely
recovered.

Obetia tenax two years after having been poisoned by picloram which leached from the roots of a tree that was treated some distance away

Once that I had noticed how very small
doses of picloram had affected other plants growing nearby I investigated what
herbicides had been sprayed in the areas where so much herbicide damage had
occurred and discovered Plenum containing Picloram has been sprayed to control
weeds in adjoining grassland. In most areas where Plenum containing Picloram
had been sprayed 100% of Trema orientalis trees had died.

Trema orientalis that has been killed by a very small amount of the herbicide picloram note the two trees growing beneath it have not been affected

Since then I have kept a very close eye on
where ever I have seen contractors spraying or applying herbicides. Time and
again I have found that Herbicides containing Picloram have caused excessive
amounts of damage and death to a number of species.

I have observed that the following trees as
extremely sensitive to very low doses of picloram

Barringtonia racemosa

Brachyleana discolor

Celtis africanus

Croton
sylvaticus

Dombeya cymosum

Ficus lutea

Grewia occidentalis

Hippobromus pauciflorus commonly known as
false horsewood

Obetia tenax

Scadoxus puniceus

Trema orientalis

Wild grape Rhoicissus tomentosa

Croton sylvaticus dying after picloram following heavy rains in an area that had been sprayed a year or two before

Research on the internet confirmed what I
had recorded but also brought to light some alarming facts as to the danger of
using Picloram in sensitive natural areas or near to them.

As a result of my own observations as well
as what information I have obtained from the internet and a number of experts
that I have discussed the danger of
applying Picloram with I will certainly never spray with any Herbicide
containing Picloram in any natural area neither would I recommend any one else
to do so.

I would go as far as to say do not under
any circumstances ever spray with any herbicide containing Picloram in
environmentally sensitive areas for instance in conservation areas or any other
area when no damage to indigenous vegetation may occur. Also do not use
herbicide gels containing Picloram and if there is absolutely no alternative
then do so with extreme caution and only on plants that cannot be controlled
with other herbicides because as reported above picloram leaches from the roots
from the roots of plants that have been treated with it killing or damaging
desirable plants growing nearby.

Barringtonia racemosa protected tree has been killed by the uninformed and careless use of picloram at the uMdloti river lagoon by an NGO doing alien plant eradication

Damage that has been cause to Barringtonia racemosa a protected tree in South Africa at the uMdloti river lagoon by an NGO doing alien plant removal

This sort of damage to the natural
environment and protected trees can be avoided

There is no need at all to use Picloram in
natural areas because there are herbicides that are just as effective and are
far safer to use so please do not use this nasty herbicide in these areas.

The following information in regards to
picloram has been published on the internet.

Picloram is a systemic herbicide that
belongs to the pyridine family of compounds, used for general woody plant
control. It also controls a wide range of broad- leaved weeds excepting
mustards (crucifers). Most grasses are resistant to picloram so it is used in
grassland management programs

Picloram can be sprayed onto foliage,
injected into plants, applied to cut surfaces, or placed at the base of the
plant where it will leach to the roots. Once absorbed by the foliage, stem, or
roots, picloram is transported throughout the plant.

Picloram is the most persistent member of
its family of herbicides which does not bind strongly with soil particles and
is not degraded rapidly in the environment, allowing it to be highly mobile and
persistent. The half-life of picloram in soils can range from one month to
several years.

As a result Picloram can move off-site
through surface or subsurface runoff and has been found in the groundwater.
Picloram may also “leak” out of the roots of treated plants, and be taken up by
nearby, desirable species.

Concentrations in runoff reported by
researchers are often adequate to prevent the growth of non-target terrestrial
and aquatic plants, and therefore, picloram should not be applied near water.

Picloram is a dicot-selective, persistent
herbicide used to control a variety of annual and perennial broadleaved herbs
and woody species. It can persist in an active form in the soil from several
months to years, and can also be released from the roots of treated plants into
the soil, where other non-target species may take it up and be injured or
killed (Hickman et al. 1989). The cut-stump treatment is typically used to
control woody species. Picloram is metabolized slowly by microbes and can be
degraded through photolysis when directly exposed to sunlight. The half-life of
picloram in soils can vary from one month to three years depending on soil and
climate conditions. Other methods of chemical degradation do not occur readily.
Picloram does not bind strongly with soils and can be highly mobile, moving to
soil depths of two meters and laterally to one km.

Soils

Picloram is not readily degraded in soils
and can be persistent and mobile. Estimates of the persistence of potentially
toxic concentrations vary from a few months to three years, depending on soil
and environmental conditions (Scrifres et al. 1972; Fryer et al. 1979; Johnsen
1980; Norris et al. 1982; Neary et al. 1985; Smith et al. 1988; Bovey &
Richardson 1991; Close et al.1998). In soils where picloram persists for long
periods of time, it has high potential to move vertically and horizontally,
which can lead to contamination of water sources and non-target (terrestrial
and aquatic) sites. Smith et al. (1988) reported that one and two years after
treating a site with 3.38 kg/ha of picloram, residues were found in the soils
and groundwater of an untreated site one km away

Water

Because picloram is water-soluble and does
not bind strongly to soil, it is capable of moving into local waterways through
surface and subsurface runoff (Michael et al. 1989). The extent to which
picloram enters a waterway depends largely on the type of soil, rates of
application, rainfall received post-application, and distance from point of
application to nearest water body or groundwater (Trichell et al. 1968; Baur et
al. 1972; Mayeux et al. 1984). In general, the larger the buffer between
treated sites and surface water bodies or groundwater, the smaller the
potential for water contamination

Vegetation

In non-susceptible species such as grasses,
picloram is metabolized rapidly, while in susceptible species, picloram can
remain intact for extended periods (WSSA 1994). When applied to soil, picloram
is readily absorbed by plant roots. When applied to foliage, the majority of
picloram (70-90%) remains in the leaves and only a small percentage is
conducted to stems and roots (Meikle et al. 1966; Cessna et al. 1989; Hickman
et al. 1990). Unabsorbed picloram remaining on leaf surfaces may photo degrade
in sunlight or be washed off with rainfall or irrigation.

Picloram absorbed by plants can be released
into the soil by passive transport through the roots and then taken up by roots
of other nearby plants (Hickman et al. 1990). Therefore, even selective
application of picloram to specific target plants could potentially harm nearby
desirable plants.

Picloram

Chemical name:
4-amino-3,5,6-trichloro-2-pyridinecarboxylic acid

Chemical class/use: chlorobenzoic acid herbicide

Picloram is sold in South Africa under the
following brand names

Grazon

Tordon

Browser

Access

Scrubber

Picloram is found in various herbicide
mixes in South Africa under the following names

There are probably other trade names of
herbicides containing picloram so please check before you apply herbicides in
sensitive areas.

References

Weed Control Methods Handbook, The Nature
Conservancy, Tu et al.

Extension Toxicology Network, A Pesticide
Information Project of Cooperative Extension Offices of Cornell University,
Michigan State University, Oregon State University, and University of
California at Davis.